Process of Treating Buchu Mercaptan Production Wastewater Using Microalgae and Chitin as a Nitrogen Source

ABSTRACT

A process of growing a culture of cyanobacteria or algae using chitin or chitosan as a source of nitrogen for photosynthetic growth is described. This process can be used to remove pollutants from nitrogen-deficient natural waters or wastewaters including buchu mercaptan production wastewater. Biomass that results from photosynthetic growth on chitin can be used, either as whole cells or the isolated components of the cells, for a large variety of commercial purposes.

CROSS-REFERENCE TO RELATED APPLICATIONS

This application is a divisional of co-pending U.S. application Ser. No.14/818,011, filed Aug. 4, 2015 which is a continuation-in-part of U.S.application Ser. No. 14/181,387, filed on Feb. 14, 2014, now U.S. Pat.No. 9,102,552 B2, issued Aug. 11, 2015, which is a divisional of U.S.application Ser. No. 13/430,486, filed on Mar. 26, 2012, now U.S. Pat.No. 8,673,619, issued Mar. 18, 2014, and claims the benefit of U.S.Provisional Application No. 61/467,869, filed Mar. 25, 2011, thedisclosures of which are hereby incorporated by reference in theirentirety including all figures, tables and drawings.

STATEMENT REGARDING FEDERALLY SPONSORED RESEARCH OR DEVELOPMENT

Not applicable.

REFERENCE TO SEQUENCE LISTING, A TABLE, OR COMPUTER PROGRAM LISTINGCOMPACT DISC APPENDIX

The Sequence Listing for this application is labeled “Seq-List.txt”which was created on Mar. 26, 2012 and is 18 KB. The entire contents ofthe sequence listing is incorporated herein by references in itsentirety.

BACKGROUND OF THE INVENTION

Chitin is one of the most abundant polymers on the planet, yet it ishighly insoluble and only a few organisms can degrade it down to simplemonomers. It is a long chain polymer of N-acetylglucosamine that isproduced by crustaceans (crabs, lobster, shrimp), mollusks, cephalopods(squid, octopus), insects, fungi, and yeasts. At present most knownchitin degraders are microorganisms that are aerobic heterotrophs. Inother words, they require oxygen to metabolize chitin as a source ofenergy, carbon, and nitrogen. Other chitin degraders require that anindependent source of organic compounds be added to the culture mediumas an energy source. Thus current schemes to use the microbialdegradation of chitin as a source for biomass or biofuel production,large scale culture conditions require abundant aeration and for theoxygen tensions to be carefully monitored and controlled. For somespecies of microorganism, an external source of carbon and energy mustbe provided (in the form, for example, of yeast extract). Both of theserequirements add significantly to the cost and energy required to carryout large-scale degradation of chitin for the purposes of biomassproduction.

A need remains for an efficient method that uses the abundant polymerchitin as a nitrogen source to produce biomass, particularlycyanobacterial or algal biomass, on a commercial scale. In order to makethe subject process as carbon neutral as possible, the method shouldreplace the use of carbon-intensive materials, such as conventionalnitrogen-based fertilizers, with carbon neutral alternatives.

BRIEF SUMMARY OF THE INVENTION

The invention is a process of growing a culture of cyanobacteria oralgae using a composition comprising chitin, an insoluble naturallyoccurring organic polymer, as a source of nitrogen for photosyntheticgrowth. This invention takes a current waste product (chitin) andconverts it into photosynthetic biomass that has a large number ofcommercial uses. Commercial uses of the biomass includes the productionof biofuels, renewable chemicals, natural pigments, nutraceuticals, feedor feed supplements for aquaculture or animals, carbohydrate componentsfor chemical feedstocks, or organic crop fertilizers, or the productionof naturally occurring sunscreen, anti-cancer, or anti-inflammatorycompounds. The subject process can also be used to remove pollutants,such as phosphorus and humic substances, from nitrogen-deficient naturalwaters or nitrogen-deficient wastewaters, such as that produced by pulpand paper industries. Because chitin is a renewable source of carbon andnitrogen (as compared to conventional sources of nitrogen fertilizers),the biomass and commercial products that result from this process areelevated onto a more carbon neutral playing field.

Wastewater from buchu mercaptan production is nitrogen-deficient. Thisproduction wastewater can be high in phosphorus and strongly acidic (dueto presence of phosphoric acid). Even if most of the buchu mercaptan isremoved for commercial production, the water still retains a strongsulfurous odor. A number of microalgal strains (all capable of rapidgrowth at acidic pH values) that grow on diluted buchu mercaptanproduction wastewater (as a phosphorus source) and chitin (as thenitrogen source) have been identified. In the processes, the strongsulfurous odor is rapidly neutralized and the algae consume thephosphorus as they grow and metabolize. Because the phosphoric acid isconsumed as a source of nutrients, the pH of the water is neutralized(from strongly or moderately acidic to near neutral pH).

BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWINGS

FIG. 1 A-D is a table of phototrophic organisms useful in the method ofthe subject invention that are able to grow on chitin as a sole nitrogensource, the table includes the origin and growth characteristics ofeach.

DETAILED DESCRIPTION OF THE INVENTION

The invention is a process by which a cyanobacterium or alga, in pureculture or in the presence of helper heterotrophs or other phototrophs,is grown using a composition comprising chitin as a source of nitrogen.This invention allows for large-scale commercial growth ofphotosynthetic biomass using a carbon neutral, renewable source ofnitrogen.

Cyanobacteria and algae use light as an energy source. Manycyanobacteria in the SYN-PRO clade, a related group that containsSynechococcus, Prochlorococcus, and Cyanobium species, as well asspecies in the Nostocales, have genes related to known chitinases intheir genomes. These organisms, however, have not yet been demonstratedin the literature as being able to grow on chitin as a sole source ofnitrogen.

Laboratory bench-scale (up to 3 liters) growth experiments show thatmany cyanobacterial taxa readily bind to purified chitin, and grow onchitin as a sole source of nitrogen. In addition, many different speciesof microalgae can grow in culture media using chitin as a sole source ofnitrogen. The presence of helper heterotrophs (which by themselves mayor may not be able to grow on chitin as a nitrogen or energy source)sometimes enhances the growth of the phototrophs in culture mediacontaining chitin. The helper heterotrophs use carbon compounds andoxygen secreted by the phototrophs and therefore an external source oforganic carbon or oxygen is not required for this heterotrophs to grow.Since many cyanobacterial cells are released from the chitin particlesinto the culture medium, the biomass that is released can be readilyharvested and used for various industrial purposes. For filamentouscyanobacteria that burrow into the solid chitin particles, biomass orbiomolecules can be readily harvested using various extractiontechniques such as those that use supercritical fluids, organicsolvents, or Soxhlet extraction.

Laboratory bench-scale experiments show that a variety of cyanobacterialtaxa (unicellular and filamentous forms) as well as small unicellularand colonial algal taxa can be isolated on chitin as the sole source ofnitrogen from enrichment cultures inoculated using a variety ofenvironmental samples such as those deriving from freshwater, seawater,evaporites (crystals from evaporated seawater), soil, and alkalinesaline lakes.

Commercial production-scale growth (2000 liters) has been accomplishedusing a selected cyanobacterium (Cyanobium) in a photobioreactor usingcrude, unpurified chitin derived from lobster shells.

The photosynthetic organisms useful in the method of the subjectinvention grow in an aqueous medium. The aqueous medium can be, forexample, tap water, well water, distilled water, reverse osmosis water,filtered water, purified water, sea water, rain water, grey water, riverwater, lake water, pond water, groundwater, or wastewater. The water canbe used unfiltered, unsterilized, or in an unpurified form.Alternatively, the water can be filtered, sterilized, or purified byrunning through ion exchange columns or charcoal filter, for example.Nutrients can be added to the aqueous medium, if they are not alreadypresent in sufficient quantities to support cyanobacterial or algalgrowth. Added nutrients can include, but are not limited to, iron,magnesium, calcium, sodium, potassium, phosphorus, sulfur, chloride, andtrace metals. The salinity and the pH of the medium can be adjusted, ifneeded, to suit that of the photosynthetic organism being used. Acomposition comprising chitin is added to the aqueous medium as thesource of nitrogen. This can be purified chitin, partially purifiedchitin, or raw unpurified chitin, that is ground coarsely or finely. Aninoculum of cyanobacterial or algal culture is added to the medium. Oneor more photosynthetic organisms may be present in the inoculum. Anexample of one method to enrich or isolate photosynthetic organismscapable of growing on chitin is provided below (Example 1). The mediumand cells are exposed to sun light, to artificial light, or a mixture ofnatural and artificial light, to allow the phototrophic cells to grow.This can be accomplished using any type of growth platform includingculture flasks, bottles, and tubes, outdoor or indoor raceway ponds,plastic bags or tubes, or a commercial photobioreactor of any design.The cells are provided a source of carbon dioxide, such as air, enrichedor pure carbon dioxide, flue or combustion gases, or fermentation gases.Some amount of time is allowed to pass, during which cyanobacterial oralgal cells divide and produce biomass. During growth the medium may ormay not be circulated using a water wheel, paddle, a pump, or by pumpingair or gas through the medium. Finally, once the desired amount ofgrowth has been achieved, the biomass is harvested.

Natural waters or wastewaters, if they have not been filtered orsterilized, can contain cyanobacteria or algae that are capable ofgrowing using chitin as a source of nitrogen. Therefore if ground chitinis added to such natural waters or wastewaters, cyanobacterial or algalbiomass can be grown in the absence of an added inoculum ofphotosynthetic organisms. Nutrients can be added to these naturalwaters, if they are not already present in sufficient quantities tosupport cyanobacterial or algal growth. The water and chitin mixturemust then be incubated in artificial or natural light, a source ofcarbon dioxide applied, and then after time has been allowed to pass thebiomass can be harvested (as described above).

The Cyanobacterium or alga may or may not be able to grow on chitin as asole source of nitrogen in pure culture. Some species or strains mayneed the presence of an additional heterotroph or heterotrophs in orderto produce photosynthetic biomass in culture media where chitin is theonly supplied source of nitrogen. In this case, the heterotrophs help tobreak down the chitin polymer, partially or completely, secretingnitrogen containing compounds that are the result of the break down ofchitin by the heterotrophs. The photosynthetic cyanobacterium or algacan then take up these break down products and use these as a source ofnitrogen to support photosynthetic growth. These heterotrophs may benaturally present in the culture medium or the culture inoculum, may benaturally present in the water or wastewaters, or they may be addedartificially to the culture medium when the photosynthetic organisms areinoculated into the culture medium. Species that have been demonstratedto grow using chitin as a source of nitrogen with or without helperheterotrophs are several related and unrelated species of cyanobacteria,green algae, eustigmatophytes, and diatoms (see FIG. 1). Other organismsthat would be useful for the invention include red algae, stramenopilesother than eustigmatophytes, dinoflagellates, cryptomonads, euglenozoa,glaucophytes, and haptophytes.

Some cyanobacterial or algal strains may prefer to grow using chitosan(a polymer related to chitin where some or many N-acetylglucosamineresidues have been deacetylated). Naturally-occurring chitin has somevarying abundance of chitosan. Thus, some photosynthetic strains may beable to be grown using ground purified chitosan, partially purifiedchitosan, naturally occurring mixtures of chitin and chitosan, orunpurified chitosan. The chitosan can be produced naturally by anorganism, enzymatically, or chemically by the artificial treatment ofchitin.

Two important industrial uses are the production of cyanobacterial oralgal biomass for a source of a slow-releasing organic fertilizer andthe production of biomass for the purposes of biofuel or biodieselproduction. Various subcomponents of the biomass can be extracted orconcentrated for industrial applications such as the production ofrenewable chemicals, natural pigments (such as carotenoids,chlorophylls, accessory light harvesting pigments, natural UV sunscreenslike scytonemin), nutraceuticals (such as omega-3 fatty acids andcholesterol-like compounds such as sitosterol), or carbohydratecomponents of the cell can be used for chemical feedstocks. Whole cellbiomass or extracted subcomponents of the biomass can be used as feed orfeed supplements for aquaculture (for example, the farming of fish orshellfish) or for animals (for example, for livestock). Organiccompounds produced or secreted by cyanobacteria grown on chitin includethe production of naturally occurring anti-cancer or anti-inflammatorycompounds.

In another preferred embodiment, the process of the subject inventioncan be used to remove pollutants, such as phosphorus, fromnitrogen-deficient natural waters or from nitrogen-deficientwastewaters, such as that produced by pulp and paper mill industries.Bench-scale experiments have shown that several chitin-utilizingphototrophic strains can grow on pulp wastewater that has undergoneprimary and secondary treatment where chitin has been added as thenitrogen source (see FIG. 1). Algal or cyanobacterial growth removespollutants from the wastewater by trapping it into biomass (see, U.S.Pat. No. 8,101,080 B2). Such pollutants could include metals,phosphorus, humic substances, and PCBs (polychlorinated biphenyls). Thebiomass can be harvested, leaving clean, or cleaner, water behind.Finally, the biomass can be harvested for use in a large number ofcommercial purposes, as outlined above. A similar method can be employedto remove pollutants from contaminated natural waters. Lakes, ponds,rivers, or groundwaters that are nitrogen-deficient but containpollutants such as phosphorus can be cleaned using a similar approach.

The advantage of using a cyanobacterium or alga to degrade chitin isthat the culture does not need to be aerated (indeed cyanobacteria andalgae produce their own oxygen). Also, an additional external carbonsource does not need to be added to the process. Light, however (eithernatural or artificial), does have to be applied to the culture chamber.

This invention provides an improved method for producing large amountsof photosynthetic biomass for commercial purposes in a renewable,sustainable fashion. One of the biggest impediments to more wide spreaduse of algae in the production of feedstocks or biofuels has been therequirement for expensive and carbon-intensive conventional sources ofnitrogen fertilizers such as urea, nitrate, or ammonia. Conventionalfertilizers have enormous carbon footprints because large amounts ofcoal are needed for their synthesis from CO₂ gas via the Haber-Boschprocess. Chitin is a waste product: most of the chitin derived from theharvesting of shellfish in the United States is currently trucked to thelandfill. The amount of chitin available for implementation as asubstrate for algal growth is therefore enormous: even a small seafoodharvester on the East Coast of Maine processes 20,000 lb of lobster meatper day. Minimal processing of chitin from crab or lobster shells canmake it a substrate for algal growth. Because the phototrophs use chitinas a source of nitrogen (and not energy), relatively small amounts ofchitin can be readily converted into large amounts of algal biomass.Shellfish are sustainably harvested, and thus the chitin that derivesfrom it is carbon neutral. Thus the invention outlined here now placeslarge-scale commercial production of photosynthetic biomass on a higher,more sustainable playing field.

A preferred embodiment of a cyanobacterium and a heterotroph that can beused in the method of the subject invention includes, but is not limitedto, a novel cyanobacterium (a close relative of Cyanobium, based on 16Sribosomal RNA sequencing) and a heterotroph (a member of theBacteroidetes) isolated from Soap Lake, Wash. Each independently growslowly on a simple mineral salts medium in the presence of chitin (seeExample 2, below). However, when grown together in a co-culture bothcells grow rapidly (doubling time of 10-11 hours) on chitin, resulting apink culture (due to the presence of chlorophyll and carotenoids in theCyanobium with abundant cells, 3×10⁷ cells/mL). This strain can alsogrow on chemically prepared chitosan in the presence of heterotrophicbacteria. Related cyanobacteria that also grow on chitin have beenisolated from the Bitterroot River, Mont., Holland Lake, Mont., and RedAlkali Lake, Wash.

Another preferred embodiment of a pure isolated cyanobacterium that canbe used in the method of the subject invention includes, but is notlimited to, a novel cyanobacterium (a close relative of Nodulariaharveyana) isolated from commercial sea salt (Celtic Sea Salt, producedby the Grain and Salt Society in Brittany, France, obtained from ahealth food store). This filamentous strain grows best on chitin as asole nitrogen source, grew well on nitrate, but somewhat poorly onnitrate, urea, N-acetylglucosamine, or in the absence of nitrogen.Related cyanobacteria that also grow on chitin have been isolated fromRed Alkali Lake, Wash., and Soap Lake, Wash.

Another preferred embodiment of a pure isolated cyanobacterium that canbe used in the method of the subject invention includes, but is notlimited to, a novel cyanobacterium (a close relative of Leptolyngbyaantarctica) isolated from Soap Lake, Wash. This filamentous strain growsbest on chitin or urea as a sole nitrogen source. It also grew well onnitrate, but somewhat poorly on ammonia or N-acetylglucosamine. Relatedcyanobacteria that also grow on chitin have been isolated fromcommercial sea salt, iron rich desert soil from Sedona, Ariz., SoapLake, Wash., and an open freshwater algae pond in Corvallis, Mont.

Another preferred embodiment of a pure isolated cyanobacterium that canbe used in the method of the subject invention includes, but is notlimited to, a novel cyanobacterium isolated from red oxidized desertsoil from Sedona, Ariz. (this strain shows only distant similarity withother cyanobacterial taxa). This strain grows best on nitrate, urea, andchitin.

Another preferred embodiment of an alga that can be used in the methodof the subject invention includes, but is not limited to, a novel greenalga (a close relative of Auxenochlorella protothecoides) isolated fromthe Bitterroot River, Mont. This alga grows best on chitin or nitrate asa sole source of nitrogen. It grows well on urea, and somewhat slowly onammonia or N-acetylglucosamine. This particular strain grows well onpulp wastewater when chitin is added to the wastewater and incubatedunder the light. Other green algal strains related to Auxenochlorellaand Chlorella that also grow on chitin have been isolated fromcommercial sea salt, Red Alkali Lake, Wash., and Soap Lake, Wash.

Another preferred embodiment of an alga that can be used in the methodof the subject invention includes, but is not limited to, a novel motilegreen alga (related to Dunaliella) isolated from commercial sea salt.This alga was purified from an isolated green colony growing on a petriplate containing chitin, and grows well on nitrate or chitin as a solesource of nitrogen.

Another preferred embodiment of an alga that can be used in the methodof the subject invention includes, but is not limited to, an alga in theEustigamtophyceae (100% identical to Nannochloropsis salina) isolatedfrom Puget Sound water. Unialgal cultures in the presence ofheterotrophic bacteria grew well on chitin. However, antibiotic treatedcultures of this particular strain that underwent serial dilution werelater shown to grow poorly on chitin. The pure alga grows best onnitrate and ammonia, grows well on urea and slowly onN-acetylglucosamine.

Another preferred embodiment of an alga that can be used in the methodof the subject invention includes, but is not limited to, a novel diatom(isolated from the Bitterroot River, closely related to Cymbella spp.).This strain grows best on nitrate, ammonia, and urea as nitrogensources. It grows well on N-acetylglucosamine, but only slowly onchitin. Other related diatom strains have been isolated from iron richdesert soil from Sedona, Ariz. and Soap Lake, Wash.

Buchu mercaptan [5-methyl-2-(2-sulfanylpropan-2-yl)cyclohexan-1-one,buchu ketone, buchu replacer, thiomenthone, para-mentha-8-thiol-3-one,mercapto-8 paramenthanone-3, p-menthene-8-thiol-3-one, and variousisomers] is a volatile organosulfur compound containing a ketone moietyattached to a hexane ring. It is used in the flavor and fragranceindustries, and has typically been derived from extracts of the Buchuplant from South Africa (Agathosma betulina). Recently, chemicalindustries are beginning to develop synthetic methods for the productionof this and related compounds (such as buchu mercaptan acetate). Thissynthetic process can result in the production of large volumes ofacidic wastewater. This wastewater needs to be treated (pH neutralized,odor removed, in some regulatory regimes the phosphorus needs to beremoved as well) before it can be discharged into the sewer or into thenatural environment.

In another preferred embodiment, the process of the subject inventioncan be used to treat wastewater from buchu mercaptan production. Anumber of microalgal strains (all capable of rapid growth at acidic pHvalues) that are capable of growing on diluted buchu mercaptanwastewater (as a phosphorus source) and chitin (as the nitrogen source)have been identified. In the processes, the strong sulfurous odor israpidly neutralized and the algae consume the phosphorus as they growand metabolize. Because the phosphoric acid is consumed as a source ofnutrients, the pH of the water is neutralized (from strongly ormoderately acidic to near neutral pH). If chitin is put in sufficientexcess in the culture, phosphorus could be largely removed from thewastewater thus eliminating any potential algal blooms that may resultwhen this wastewater is discharged into the environment. Phosphorus isincreasingly being regulated as a pollutant by the U.S. EnvironmentalProtection Agency, so efficient and natural methods of reducingphosphorus pollution from wastewater sources are becoming increasinglydesirable.

In a particularly preferred embodiment, microalgae growth is optimizedin the subject process by diluting the buchu mercaptan wastewater. Inthe exemplified embodiments, the wastewater was diluted 0.1%. Dilutionscan be made with material including, but not limited to, culture medium,other waste waters, or just water. One skilled in the art wouldunderstand that optimizing dilutions will vary with the strain of algaeused as well as with the origin and type of wastewater and optimizingalgael growth within the claimed process is well within the skill of theart.

The biomass produced through the process of wastewater treatment is avaluable commercial commodity. The biomass can be harvested and useddirectly as a feed supplement for aquaculture or for animal feed.Biomass components can be separated and sold individually. Such biomasscomponents include oils (biofuels), proteins, natural food pigments,nutraceuticals (such as omega-3 fatty acids), and algae extracts forcosmetics and personal care products. The revenue generated from thesale of these bioproducts can help to offset the costs associated withthe algal/chitin wastewater treatment system.

Growth of algae on wastewater (as the phosphorus source) and wastechitin (as the nitrogen source) means that algal biomass can be grownusing low-cost sources of macronutrients. It also means that thegreenhouse gas and energy footprints for the production of algal biomasscan be greatly diminished. Conventional fertilizers (ammonium phosphate,ammonium nitrate, urea) have enormous greenhouse gas and energyfootprints, because these compounds are synthesized using theHaber-Bosch process. Large amounts of fossil fuels are needed to carryout the Haber-Bosch process. The decreased greenhouse gas and energyfootprints of the resulting biomass and biomass products make thesebioproducts more desirable.

The following examples are offered to further illustrate but not limitboth the compositions and the methods of the present invention. Allpercentages are by weight and all solvent mixture proportions are byvolume unless otherwise noted.

Example 1—General Enrichment Culture and Strain Isolations

An example scheme for the enrichment of cyanobacterial or algal strainsthat grow on chitin is presented as follows.

Nitrogen-free culture medium that replicates or mimics the environmentalconditions in which the water or surface sediment sample comes from isprepared and autoclaved. Example culture media includes BG-11 for theisolation of freshwater strains and ASN III for the isolation of marinestrains. The media recipes are modified so that they omit any form ofadded nitrogen (nitrate or ammonia). Purified, ground, autoclaved chitinis added to the medium to the approximate final concentration of 0.5% ina sterile culture flask or bottle. One or several milliliters of freshlyobtained water and/or surface sediment is added to the culture flask asthe inoculum. This enrichment culture is incubated under the light(either natural sunlight or artificial light) until photosyntheticorganisms appear (takes anywhere from 1-8 weeks). Cultures may or maynot be shaken. Initially, heterotrophic bacteria and heterotrophiceukaryotes appear in the culture. However, it generally takes muchlonger incubation times before phototrophic cyanobacteria and algaebegin to appear in the enrichment culture. Once phototrophic organismsbecome numerous, and either the chitin particles become colonized withpigmented cells or the aqueous medium becomes colored from abundantphototrophic growth, the phototrophs can be purified to obtain unialgalcultures using conventional microbiological techniques. Theseconventional techniques include serial dilution in medium that containsdifferent sources of nitrogen (for example serial dilution on mediumcontaining nitrate). Most resulting cultures are unialgal, in that theycontain one phototrophic species but may contain one or severalheterotrophic bacterial species. Pure cultures can be obtained bystreaking petri plates that contain chitin or other sources of nitrogen.Antibiotic treatment alone or in combination with serial dilution can beused to reduce or eliminate the number of heterotrophic bacterialspecies in the culture. However, presence of the heterotrophic bacteriamay aid photosynthetic growth on chitin, depending on the individualstrain.

Example 2—Sampling, Enrichment Culture, and Isolation of Cyanobium

Five liters of surface water was collected from Soap Lake, Wash. on Mar.28, 2010. The temperature of the water was 11.6° C., the pH was 9.83,and the conductivity was 23 mS. The water sample was transported back tothe laboratory in Missoula, Mont. and was used to inoculate 25 mLculture media in 250 mL culture flasks that were incubated under afull-spectrum plant light at 18° C. The culture medium (Soap Lakeautotrophic medium) contained (per liter): 1.5 g NaCl, 3.4 g NaHCO₃,2.85 g NaCO₃, 0.95 g Na₂HPO₄, 2.5 g Na₂SO₄, 0.95 g KCl, 0.035 g KNO₃,0.01 g NH₄Cl, 1.5 g CaSO₄*2H₂O, 2.45 g MgCl₂*6H₂O, 2.5 mL 1 mM EDTA, 2.5mL ammonium-iron solution (1 mM NH₄Cl, 1 mM Fe(III)Cl₃, 2.5 mM sodiumcitrate, 0.025 N HCl) and 1 mL trace metal solution (per liter: 2.86 gboric acid, 1.81 g MnCl₂*4H₂O, 0.222 g ZnSO₄*7H₂O, 0.39 g NaMoO₄*2H₂O,0.049 g CoCl₂*6H₂O), pH adjusted to 9.5. Measurement of cyanobacterialgrowth was monitored by red chlorophyll autofluorescence using a Nikonepifluorescence microscope at 400× magnification. A culture with asingle cyanobacterium and a heterotroph was obtained by serial dilutionsto extinction. A pure culture of the cyanobacterium was obtained byrepeated serial dilution in culture medium that omitted sodium citrate.Elimination of the heterotroph was confirmed by Live:Dead (MolecularProbes, Invitrogen) fluorescence staining. A pure culture of theheterotroph was obtained from an isolated colony grown on Soap Lakeautotrophic medium containing agar.

After 4 days' incubation, small, non-motile cocci that exhibited redchlorophyll autofluorescence were observed in the enrichment culture,consistent with the size and morphology of small-diameter Synechococcusand Cyanobium species. No cyanobacteria were observed in enrichmentmedia where copper was present in the trace element solution. Aftermultiple serial dilutions to isolate the cyanobacterium, it was observedthat the culture contained two microorganisms—the cyanobacterium plus anon-photosynthetic heterotroph. To isolate the cyanobacterium in pureculture, multiple aggressive serial dilutions were performed in mediumthat lacked organic carbon. Elimination of the heterotroph was confirmedby staining the cells with the green stain from the Molecular ProbesLive:Dead kit (which stained the heterotroph but not thecyanobacterium). Dense cyanobacterial cultures had a slight pinkish hue,and the accumulation of cells that sank to the bottom of the culturetube were a pinkish burgundy.

When plated on autotrophic medium containing agar, the heterotroph grewslowly, producing circular colonies that were 2-3 mm in diameter, had asomewhat irregular border, and were orange in color. Colonies grewequally well on plates incubated in the dark as the light. Cellsoccurred as cocci singly or in pairs as a result of binary fission, andwere non-motile. The co-culture was reconstituted by mixing the purecyanobacterium with heterotroph cells from an isolated colony. Theresulting co-culture cell suspension was a moderate pink in color as aresult of cyanobacterial growth.

In pure culture the exemplified Cyanobium grows well on nitrate and ureaas a sole carbon source, and only weakly to poorly using ammonia. Itgrows poorly in the absence of added nitrogen, however this is likelydue to trace impurities of nitrogen in either the culture reagents orthe glassware (PCR results did not result in the amplification of a genefor nitrogenase). In pure culture, the exemplified Bacteroidetesheterotroph grows very poorly in the absence of spent culture mediumfrom an old Cyanobium culture. Thus, the heterotroph likely uses organiccompounds (unidentified) released by the Cyanobium into the culturemedium as an energy source, as well as using the oxygen produced by theCyanobium as a terminal electron acceptor.

The subject Cyanobium grows well under a wide variety of pH and salinityvalues. The optimal pH of growth was 9.0, however measured growth rateswere significantly high between pH 7 and 10. The upper limit of growthwas pH 10.5 (no growth at pH 10.5). The optimal salinity of growth was0.6% NaCl, however growth rates were significant from 0.04% to 3% NaCl.Growth also occurred at 5% NaCl, however growth rates were lower.

Example 3—Enrichment and Isolation of Nodularia and Nostocales spp.

Commercial sea salt crystals were dissolved into N-free ASN III mediumcontaining purified chitin and incubated at room temperature underartificial light. After several weeks, small intensely green clumpsappeared on the chitin particles. Microscopic examination showed thatthese were colonies largely made of filamentous, heterocyst- orakinete-forming cyanobacterial filaments that belong to the Nostocalesfamily. Enrichments of related cyanobacteria were also obtained from RedAlkali Lake, Wash., and from Soap Lake, Wash. Enrichment cultures,however, proved difficult to purify the Nostocales spp. from otherphototrophs by serial dilution, even in culture medium lacking nitrogen(these strains are capable of fixing nitrogen and hence grow slowly innitrogen-free media). Pure cultures were obtained by plating on solidmedium containing nitrate or ammonia.

Example 4—Enrichment and Isolation of Leptolyngbya spp.

Commercial sea salt crystals were dissolved into N-free ASN III mediumcontaining purified chitin and incubated at room temperature underartificial light. After several weeks, long, thin cyanobacterialfilaments were observed microscopically using epifluorescence to begrowing inside the chitin clumps. Eventually, this resulted in clumpingof the chitin particles and the particles turning green.

For Leptolyngbya enrichments from Sedona soil or Soap Lake water, it wasvery difficult to obtain a unialgal culture by repeated serial dilution,even if the filaments were washed with nitrogen-free medium prior toserial dilution. Pure cultures were obtained by plating on solid mediumcontaining nitrate or urea.

Example 5-Sampling, Enrichment Culture, and Isolation of NovelCyanbacterium

Iron rich desert soil containing a microbial cryptobiotic crust inSedona, Ariz. was sampled on Feb. 5, 2011. Material was transferred intoNitrogen-free BG-11 medium containing chitin as a nitrogen source andincubated under artificial light for several weeks. This resulted in anenrichment culture containing a diverse array of heterotrophs,cyanobacteria, and diatoms. Material was serially diluted on an array ofdifferent nitrogen sources (nitrate, ammonia, urea, and chitin). Eachdilution was periodically examined and rediluted in order to isolatethree cyanobacterial and one diatom strain. One cyanobacterial strainwas observed to grow as paired rods. This strain grew well on nitrate,urea, and chitin as nitrogen sources. 16S ribosomal DNA sequencingshowed that this strain is only distantly related to any knowncyanobacteria (95% identical to Acaryochloris), and thus could comprisea novel genus or family.

Example 6—Sampling, Enrichment Culture, and Isolation of Auxenochlorellaspp.

Surface water from the Bitterroot River was sampled from the boat launchat McClay Flat on Apr. 17, 2011, before the spring run off. The watertemperature was 9.5° C. and the pH was 6.99. Water was inoculated intoN-free BG-11 medium containing purified chitin and incubated for severalweeks at room temperature under artificial light. Serial dilutions ofthe resulting enrichment culture on nitrate, ammonia, or urea led to theisolation of one cyanobacterium, a diatom, and a green microalga withmorphology similar to Chlorella. 16S ribosomal DNA sequencing of thechloroplast genome showed that the green microalga was most closelyrelated (98% identical) to Auxenochlorella protothecoides.

Additional Chlorella like strains have been isolated by enrichment onchitin followed by serial dilution from Red Alkali Lake, Wash., and SoapLake, Wash. Similar strains have also been observed in enrichmentcultures from various coastal marine waters collected around the UnitedStates.

Example 7—Enrichment Culture, and Isolation of Dunaliella spp.

Commercial sea salt crystals were dissolved into a modified Haloarculamedium (a hypersaline medium lacking organic carbon and nitrogen, withadded phosphate, iron and trace elements) containing purified chitin andincubated at room temperature under artificial light. After severalweeks, a pink enrichment culture resulted which contained abundant cellsfrom the Halobacteriaceae as well as flagellated green microalgae withmorphological features characteristic of Dunaliella. Streaking of theenrichment culture onto modified Haloarcula medium containing agar andchitin resulted in a small number of isolated dark green colonies andabundant pink colonies. The dark green colonies were comprised ofDunaliella cells and the pink colonies were comprised of archaea in theHalobacteriacaea. A single Dunaliella colony was transferred into liquidmedium containing 1 mM nitrate. Growth was found to occur on marinemedium (N-free ASN III with chitin), however growth in hypersalinemedium resulted in higher cell densities.

Example 8—Sampling, Enrichment Culture, and Isolation of Nannochloropsisspp.

Seawater from the Puget Sound was collected in shallow water off on Nov.27, 2010 from a public beach near Point Wilson Lighthouse, PortTownsend, Wash. This was inoculated into 25 mL N-Free ASN III mediumcontaining 0.5% chitin, incubated at room temperature under artificiallight. This strain did not grow well autotrophically in ASN III mediumlacking chitin, but grew well in medium with chitin, nitrate, ammonium,or urea as the source of nitrogen. Antibiotic treatment (usingkanamycin, chloramphenical, and spectinomycin) and serial dilution,coupled with growth on nitrate, was used to eliminate most of thebacteria in the original enrichment culture. The resultingantibiotic-treated strain grew well on nitrate, ammonia, or urea, butgrew less well on chitin. Thus, heterotrophs likely enhance the growthrate of the organism on chitin. 16S ribosomal RNA analysis showed thatthis strain was 100% identical to Nannochloropsis salina.

Enrichment cultures of N-Free ASN III medium containing chitin,established from a wide variety of inocula from across the United Statesresulted in mixed cultures that contained Nannochloropsis and bacterialheterotrophs.

Example 9—Enrichment Culture and Isolation of Cymbella spp.

Enrichment cultures obtained from water from the Bitterroot River,Mont., contained diatoms (see also Example 6, above). The diatoms werepurified by serial dilution in the presence of antibiotics. Sequencingof the chloroplast 16S ribosomal DNA gene shows that this alga is 97%identical to Cymbella pisciculus. Other diatom strains have beenisolated from chitin grown enrichments from iron rich desert soil fromSedona, Ariz., and from alkaline Soap Lake, Wash. 16S ribosomal RNAshows that these three diatom strains are all very closely related,belonging to the genus Cymbella.

Example 10—Growth of Algal Strains on Diluted Buchu ProductionWastewater with Chitin

Buchu mercaptan production wastewater was diluted to 0.1% (pH 2.93,about 1 mM phosphate) using a modified synthetic culture medium(phosphorus-free, nitrogen-free BG-11 providing minimal cation andanions to support growth of freshwater microalgae). The pH of themixture was adjusted to 4.2 and 4 cultures were set up. The firstculture was a control with phosphorus-free BG-11 containing nitrate asthe nitrogen source. The second culture contained 0.1% buchu mercaptanproduction wastewater in P-free N-free BG-11 where nitrate was thenitrogen source. The third culture contained 0.1% buchu wastewater inP-free N-free BG-11 where chitin was the nitrogen source. The cultureswere inoculated with a mixture of three acidophilic algal cultures (aChlamydomonas-like strain, a Chlorella-like strain, and anuncharacterized green microalgal strain). After several days'incubation, the first (control) culture showed growth of all threestrains. The second culture showed little algal growth, and had a strongodor. The third culture showed moderate algal growth, and had no odor.After longer incubation, the pH of the tubes was measured. The positivecontrol tube showed the pH had increased (from 4.2 to 6.8). Tube 2showed only a small increase in pH (from 4.2 to 5.0). Tube 3 showed anincrease in the pH (from 4.2 to 6.6).

Example 11—Growth of Additional Algal Strains on Diluted BuchuProduction Wastewater with Chitin

Buchu mercaptan production wastewater was diluted as in the previousexample with P-free N-free BG-11 synthetic culture medium (pH adjustedto 4.2). The first culture contained nitrate as the nitrogen source andwas inoculated with algal mix #1 (a Chlamydomonas-like strain, aChlorella-like strain, and an uncharacterized green microalgal strain).The second culture contained nitrate as the nitrogen source and wasinoculated with algal mix #2 (a green alga in the Coccomyxaceae, asecond Chlorella-like strain, and an uncharacterized filamentous greenalga). The third culture contained chitin as the nitrogen source and wasinoculated with algal mix #1. The fourth culture contained chitin as thenitrogen source and was inoculated with algal mix #2. After severaldays' incubation, the tubes with nitrate as a nitrogen source showedlittle or no algal growth. However, the tubes with chitin as thenitrogen source were green and showed moderate algal growth. The tubeswith nitrate as the nitrogen source had a strong odor, whereas the tubeswith chitin as the nitrogen source had no odor. After additionalincubation, the Chlorella and Coccomyxaceae strains showed the bestgrowth, again with chitin as the nitrogen source. The tubes with nitrateas the nitrogen source showed a slight increase in pH (from 4.2 to 4.9and 5.1). The tubes with chitin as the nitrogen source showed anincrease in pH (from 4.2 to 6.4 and 6.5).

Example 12—Growth of Additional Algal Strains on Diluted BuchuProduction Wastewater with Chitin

Buchu mercaptan production wastewater was diluted to 0.1% with P-freeN-free BG-11 synthetic medium where the pH was not adjusted (the pH ofthis water was 2.8). Two algal strains were tested (a Chlorella-likestrain, and a strain in the Coccomyxaceae). Three nitrogen sources weretested (ammonia, nitrate, and chitin). After several days' incubation,there was little algal growth in the tubes with ammonia and nitrate.There was a strong odor of buchu mercapan in these tubes as well. The pHof these tubes ranged from 2.85 to 2.91. The tubes with chitin, on theother hand, showed moderate to good algal growth and had no buchumercaptan odor. These tubes had pH values of 6.0 and 6.4.

It is understood that the foregoing examples are merely illustrative ofthe present invention. Certain modifications of the articles and/ormethods employed may be made and still achieve the objectives of theinvention. Such modifications are contemplated as within the scope ofthe claimed invention.

1. A method of producing biomass comprising the steps of: collecting wastewater, wherein the wastewater is from the industrial production of a component selected from the group consisting of buchu mercaptan and buchu mercaptan acetate; adding a composition comprising at least one polymer selected from the group consisting of chitin and chitosan to the wastewater: inoculating the wastewater with at least one photosynthetic organism that uses chitin or chitosan, or a breakdown product of chitin or chitosan metabolism in the composition as a nitrogen source; exposing the inoculated wastewater to light; exposing the inoculated wastewater to carbon dioxide; detecting growth of the at least one photosynthetic organism that uses chitin or chitosan, or a breakdown product of chitin or chitosan metabolism as a nitrogen source; and harvesting the at least one photosynthetic organism for biomass.
 2. The method of claim 1, wherein said method further comprises the step of diluting said wastewater after it is collected.
 3. The method of claim 1, wherein said at least one photosynthetic organism that uses chitin or chitosan, or a breakdown product of chitin or chitosan metabolism, as a nitrogen source is an alga.
 4. The method of claim 1, wherein said alga is selected from the group consisting of green algae, red algae, eustigmatophytes, diatoms, stramenopiles, dinoflagellates, cryptomonads, euglenozoa, glaucophytes, and haptophytes.
 5. The method of claim 1, wherein said chitin is selected from the group consisting of ground purified chitin, partially purified chitin, and unpurified chitin.
 6. The method of claim 1, wherein said chitosan is selected from the group consisting of ground purified chitosan, partially purified chitosan, unpurified chitosan, naturally occurring chitosan, chemically prepared chitosan, enzymatically prepared chitosan, or mixtures thereof.
 7. The method of claim 1, wherein said light is selected from the group consisting of sun light, artificial light, and mixtures thereof.
 8. The method of claim 1, wherein said carbon dioxide is from a source selected from the group consisting of air, enriched carbon dioxide, pure carbon dioxide, flue gas, combustion gas, and fermentation gas.
 9. The method of claim 1, further comprising the step of circulating the inoculated wastewater.
 10. The method of claim 9, wherein the inoculated wastewater is circulated by aeration or an implement selected from the group consisting of a water wheel, a paddle, and a pump.
 11. The method of claim 1, wherein said method further comprises the step of after inoculating the wastewater with the at least one photosynthetic organism that uses chitin or chitosan, or a breakdown product of chitin or chitosan metabolism as a nitrogen source, further inoculating the wastewater with a heterotroph that supports the growth of the at least one photosynthetic organism that uses chitin or chitosan, or a breakdown product of chitin or chitosan metabolism as a nitrogen source.
 12. The method of claim 1, further comprising the step of adding at least one nutrient to the wastewater that is not a source of nitrogen, the nutrient selected from the group consisting of iron, magnesium, calcium, sodium, potassium, phosphorus, sulfur, chloride, and trace metals. 